Assessment of The Degree of Conformity of Existing Land Use  
Patterns of Calabar Metropolis with the 1973 Calabar Urban Master  
Plan  
Obongha, Ukpali E.; Bassey, Obasesam C.; Mfah, Christian N.  
Department of Urban and Regional Planning, University of Cross River State, Nigeria  
Received: 21 November 2025; Accepted: 28 November 2025; Published: 03 December 2025  
ABSTRACT  
Land use conformity with the master plan of any urban environment is critical as it encourages spatial segregation  
of activities leading to environmentally sustainable developments. This study assessed the difference between  
the existing land use patterns of Calabar Metropolis and the 1973 Calabar urban master plan. This was done by  
postulating a null hypothesis that there is no significant difference between the existing land use patterns of  
Calabar Metropolis and the 1973 Calabar urban master plan. The study adopted a survey design method with  
qualitative and quantitative approaches. Qualitative approach involved a combination of interviews and  
questionnaire administration and weighted on the Likert Scale while quantitative approach used data obtained  
from map analysis on X1 and X2 variables depicting existing land use patterns and the 1973 Calabar urban Master  
plan. The One-Way ANOVA was applied in the test statistic and the result showed a significant relationship.  
This result pointed to the fact that there is no controlled development in Calabar Metropolis because the planning  
authority has been handicapped without facilities needed to function optimally. The study therefore,  
recommended for strengthening of the planning authority as well as urgent review of the master plan.  
Key Words: ANOVA; Conformity; Controlled development; Existing land use patterns; Likert scale; Map  
analysis; Master plan.  
INTRODUCTION  
Land use conformity is simply the degree to which two or more land uses, such as residential, commercial, and  
recreational for example, coexist as zoned in the master plan without a significant negative impact on each other  
and the residents (Cengiz, 2013). Land use conformity brings about functional segregation, in that one land use  
type such as residential has a positive impact on the other, for example, commercial land use as indicated in the  
zoning ordinance of the master plan. Non-conforming land use on the other hand, could be seen as the use to  
which a particular land is put, as opposed to the use designed in the zoning ordinance of the current master plan.  
In the earliest days of zoning all uses were classified very simply by a “hierarchy of uses” into three major  
districts or zones such as residential, commercial and industrial or manufacturing (Cengiz, 2013). Residential  
uses included living areas with a few other essential facilities such as churches, schools and depots. Facilities  
allowed in the residential zones were also permitted in commercial zones. Manufacturing was a catch-all for  
every kind of use including manufacturing, commerce and housing for the low-income people who could not  
afford to live elsewhere (Cengiz, 2013; Duany and Tallen, 2002).  
Non-conforming land uses also exist in African cities such as Cairo, Johannesburg, Pretoria, Kisii, Nwanza, Dar  
Salaam, Abuja, Kano, Lagos, Port Harcourt, Umuahia and others. In the city of Cairo, Egypt for example, zoning  
regulation is enshrined in the master plan with establishment of strong institutions that monitor compliance with  
the master plan and controlled development. The Tourism Development Authority (TDA) for example, monitors  
all developments related to tourism while the New Communities Development Authority (NCDA) monitors all  
residential and institutional developments. Other developments for example, industrial and commercial also have  
their respective agencies. These agencies are answerable to the Town Planning and Engineering Department  
who gives planning permits for all development and redevelopment activities. Despite all these agencies  
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monitoring and controlling physical developments, non-conforming land uses exist in patches as relics of  
historical and cultural districts that predated their respective zoning regulations (Ahmed and Abd-Elkawy, 2020).  
In Kisii city of Kenya, according to Omollo (2019) Kisii got its master plan in 1972 and by 2005 after thirty-  
three years, there were serious distortions in the zoning regulation of the 1972 master plan that resulted in  
injurious and non-conforming land uses. However, currently, these non-conforming land uses coexist between  
one and the other. In Abuja, Nigeria, for example, non-conforming land uses exist in the Federal Capital Territory  
(FCT). Studies have shown that the Abuja Master Plan was prepared in 1970 and the central area was designed  
by a Japanese Architect, Kenzo Tange to accommodate all the land uses including residential, institutional,  
administrative, commercial, industrial, recreational, and circulation. Non-conformity of land uses was obvious  
in the late 1990s despite demolition exercises embarked on by the then Minister of the FCT between 1999 and  
2007. The Abuja Master Plan of 2008 was also established as a review of the 1970’s master plan (Nor, 2017).  
This review was done basically to curb non-conforming land uses which are still in existence. Reports have  
shown that the present Minister of the FCT has earmarked and named for demolition several zones of non-  
conforming land uses in the FCT.  
Other Nigerian cities such as Kano, Lagos, Port Harcourt, Owerri, Umuahia, and Enugu have experienced series  
of demolition exercises by successive governments in order to reduce the impact of non-conforming land uses  
and distortions of their master plans. Ibrahim and Mai, (2020); Godswill, Nnaemeka, and Ukachukwu, (2017)  
have shown that institutional decay (especially among institutions and agencies responsible for urban land use  
administration), lack of political will and administrative deficiencies in enforcing compliance with their  
respective master plans are some of the factors responsible for persistence of non-conforming land uses in  
Nigerian cities.  
In Calabar Metropolis, some of the insensitivity in urban land use planning has led to some patterns of land use  
antagonism. Non-conforming land uses seem to exist in all the neighbourhood zones of Calabar Metropolis. For  
example, within the spectrum of what is generally defined as a particular land use such as a residential zone, is  
often interspersed with pockets of other uses which are remnants of socio-cultural land use practices, especially  
in the old unplanned neighbourhoods of Calabar Metropolis. In some of the neighbourhoods of Calabar  
Metropolis, land use may be chaotic and serious efforts may have to be made to clearly discern the types and  
sub-types. The difficulty here lies in the fact that the parameters to be used in delineating the sub-types may be  
spatially invariant and as such, not sufficiently discriminatory as to produce distinctive classes (Obongha, 2024).  
This happens because institutions responsible for land use planning lacks political will resulting in non-  
compliance with the existing master plan particularly by those with political power.  
From the foregoing, it is obvious that land uses in Calabar Metropolis are inappropriately intermixed with  
residential zones and without compliance with the Calabar urban master plan of 1973, and as such, have  
destroyed the aesthetics of the city landscape. Non-conforming land uses are sometimes, potential health hazards.  
There are several negative effects documented by many studies for converting one land use type to the other as  
well as destroying the urban milieu (Foreman, Reineking, and Hersperger, 2002). Decisions on land uses can  
have profound consequences both positive and negative, subject to the views and values of the affected  
residents. This study attempts a deep examination of critical issues on land use pattern in a city of a developing  
country, Calabar Metropolis, Nigeria.  
The study is however, aimed at assessing the difference between the existing land use patterns and those  
contained in the 1973 Calabar urban master plan. This aim was achieved by testing a null hypothesis that there  
is no significant difference between the existing land use patterns of Calabar Metropolis and the 1973 Calabar  
urban master plan  
The Master Plan  
According to Kumar (2017) the master plan is a comprehensive plan that integrates various aspects of planning  
such as land use, housing, transportation, infrastructure, and development control. The comprehensiveness of  
the master plan, therefore, embraces all aspects which are necessary to improve the socio-economic  
characteristics and quality of life of the people. The master plan is multidisciplinary in nature and encompasses  
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thoughts and practices from the social sciences, economics, geography, urban planning, environmental sciences,  
engineering, architecture and surveying. The master plan is a long-term document that maps out development  
for future, as well as clears out the vision for perspective year of a city. The master plan focuses on rational use  
of the land and utilized optimally for the various activities that take place in a city. The proposals for a master  
plan development are usually environmentally sustainable and based on inclusive planning. The master plan  
concept however, encourages spatial segregation of land uses and clustering of similar land uses.  
The master plan includes ideas from all sections of people in the community in its development proposals and  
focuses on the following principles: (i) affordability (ii) restrictions on ecologically sensitive areas (iii) heritage  
sites and traditional build up areas and gives special norms for such areas and (iv) balanced growth of the city.  
The master plan emphasises zoning and prevents concentration of injurious land uses/activities in a particular  
location. It takes into account appropriate distribution of facilities, infrastructure, networks, housing, and follows  
neighbourhood concept development. The master plan is an instrument to work out land and infrastructure  
requirements for various urban and rural areas, and allocate land for various uses to result in harmonious and  
sustainable distribution of activities so that towns/cities are provided with a form and structure within which  
they can perform all their economic and social functions efficiently and effectively. The purpose of a master  
plan is to promote growth, guide and regulate present and future development of towns and cities with a  
perspective of 20-25 years (Kumar, 2017).  
The Hampshire Planning Commission (2021) lists the characteristics of the master plan as follows: (i) physical  
plan: the plan as a fundamental guide to the physical development of the city; (ii) long ranged activities involving  
long term planning; (iii) comprehensiveness encompassing all the functions that make a city work, such as  
transportation, housing, land use, utility systems, and recreation. In addition, the master plan provides (iv) the  
interrelationships of functions; (v) a guide to decision making for the planning board, the governing board and  
mayor or manager; (vi) a statement of public policy which translates community values, desires, and visions into  
land use and development principles that can guide the future growth of the city.  
The master plan has been modeled by the researcher from the New Hampshire Planning Commission as shown  
in Figure 1.0. The model explains various dimensions and elements of the master plan including its impact on  
urban land use planning and the socio-economic characteristics and improvement of life of the residents of a  
particular city. Its comprehensiveness also includes population projection and economic activities performed by  
the residents. It integrates long term and multidisciplinary programmes.  
Figure 1.0: Model of the master plan concept  
Source: Modelled from the Hampshire planning commission  
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In the application of the master plan for sustainable urban land use planning, Neamtu (2011) conducted a study  
in Romania using two methods. Firstly, interviews were conducted with 25 Town Planners working for the city  
council. Secondly, a number of 40 master plans were accessed in order to assess whether they meet the principles  
and objectives of sustainable development. The results of the study showed that majority of these master plans  
were prepared without involving the stakeholders from within the community and not also synchronizing with  
the national or regional plans. There were also elements of the verbal policy plans which seem to be unusual.  
This is so because they represent a drastic departure from the urban plans and contain very few or no statistical  
data and maps. Rather, they basically focused on a vision statement and strategic objectives of the city.  
Kasala (2015) conducted similar research on the return to master planning in Dar es Salaam, East Africa. The  
study applied two methods. First, researcher reviewed secondary data which comprises many years of Dar es  
Salaam strategic/structure plans. Second, the researcher interviewed professionals in the academia, planning  
institutions, local authorities, and NGOs with a questionnaire. The result of the study showed that several master  
plans of Dar es Salaam were prepared and were never implemented. Failure to implement the mater plans  
resulted in the introduction of alternative approach to planning, known as Strategic Urban Development Planning  
(SUDP). The study concluded that the SUDP was eventually returned to master planning due to misconceptions.  
The return persisted in the sense that the key stages of SUDP which include introduction, plan formulation,  
content determination and interpretation into actions were done in the context of laws and procedures of the  
master plan.  
Nallathiga (2016) investigated the role of Master Plans in city development in India, using the methodology of  
systematic reviews. The concepts and methods of traditional master planning in India owe its origin to British  
town planning laws. The importance of master plans has primarily been confined to the aspects of land use  
planning, physical infrastructure, and development control. The study by Nallathiga (2016) highlighted the role  
of master planning to include a design for the physical, social and economic development of the city, and also  
to improve the quality of life as well. The master plan performed functions as follows: (i) to guide the  
development of the city in an orderly manner so as to improve the quality of life of the people, (ii) to organize  
and coordinate the complex relationships between urban land uses, (iii) to chart a course for growth and change,  
(iv) to be responsive to change and maintain its validity over time and space, and be subject to continual review,  
(v) to direct the physical development of the city in relation to its social and economic characteristics based on  
comprehensive surveys and studies on the present status and the future growth prospects, and (vi) to provide a  
resource mobilization for the proposed development works.  
Uncontrolled developments taking place in Calabar Metropolis have raised several professional concerns as to  
whether there is an existing master plan which guides development or not. In 1973, the administration of U. J.  
Esuene saw the need for Calabar urban master plan and engaged TESCO-KOZTI Consulting (Nig.) Ltd., a town  
planning firm based in Hungary but with office in Calabar, Cross River State, Nigeria. The Calabar urban master  
plan was to address some key areas such as effective land use planning. It was also to overcome the challenges  
of development control with emphasis on demographics and socio-economic characteristics of the residents.  
Other details of the master plan were to include population and land use projections to the year 1998. It was  
proposed that the master plan would be reviewed after twenty-five years, from 1973 to 1998. However, the  
proposal of the master plan terminated at the present-day Army Junction (welcome to Calabar) and other new  
zones such as Ikot Effangha Mkpa, Ikot Eneobong, Ikot Omin and Ikot Ekpo were not captured in the Calabar  
urban master plan of 1973. In 1998, the Calabar urban master plan was not revised due to frequent changes in  
administration during the Military era.  
In 2000, the then Governor of Cross River State invited a team of indigenous Town Planners to revisit and review  
the Calabar urban master plan of 1973. A contract was awarded and projections were made to 2020. Some of the  
important areas to be revised were: the relocation of the Watt Market and the Margaret Ekpo International  
Airport. The proposal to relocate the Watt Market, for example, brought about tension within Calabar Metropolis  
to the point that the Efik women came out nude to protest the relocation plan. Their argument was that the  
location of Watt Market at the present position was ancestral and all of them including their ground parents were  
born to meet the Watt Market at that present location.  
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Unfortunately, the 2000 Calabar urban master plan policy document has been reported missing and could not be  
found or traced in the Ministry of Lands, nor in its affiliates such as the Departments of Town Planning and  
Surveys. Now, it is the 1973 policy document that is available in the Town Planning Department of the Ministry  
of Lands. But this document does not cover the present Calabar Metropolis. In 2012, the then Governor of Cross  
River State made attempt to review the 1973 and 2000 Calabar urban master plans and renamed it the Greater  
Calabar Master Plan (to cover all parts of Calabar Metropolis including Ikot Effangha Mkpa, Ikot Omin, Ikot  
Eneobong, and Ikot Ekpo). The government engaged the Canadian Pacific Consulting Services (CPCS) and  
made commitment to the tone of 1,200,000,000.00 USD for the project (Obongha & Bassey, 2025). CPCS  
commenced the plan preparation and made public hearing with several presentations to the Officials of Cross  
River State Government, professional bodies, and the general public. Regrettably, the administration that took  
off from May, 2015 failed to follow up with the Greater Calabar Master Plan project despite several push from  
the Town Planning Professionals and the CPCS. On January 24, 2018 the Governor inaugurated an eight-man  
task force on development control leaving the Town Planning Professionals idle and redundant. The task force  
was to handle development control, based on the observed distortion of the master plan which was going on at  
a very fast rate, and that people were building houses without approved plans. Others were erecting industrial  
buildings in residential zones, building residential accommodation in flood plains and without respecting the  
building lines between highways, roads and clearance as stipulated in the Federal Highway Codes (Obongha &  
Bassey, 2025).  
Despite this observation, the 2015-2023 administration brought development control to a halt, land use planning  
virtually ceased, and many open spaces left as green areas in the 1973 and 2000 master plans were built up. In  
fact, the administration injected so many counterpart agencies into land use planning, many of which were non-  
professionals which allowed any form of development at any location, whether conforming or non-conforming.  
Demolition exercises which used to be conducted by the Directors of Town Planning in the previous  
administrations could no longer take place in Calabar Metropolis (Obongha & Bassey, 2025). Public/institutional  
lands such as the University of Cross River State, Calabar Campus experienced over thirty per cent of its land  
being built up by invaders (Obongha, 2024). The year 2000 Calabar urban master plan recommended for a review  
after 20 years (that is in 2020) but, was not reviewed despite efforts by the previous administrations to review  
the master plan and renamed it “Greater Calabar Master Plan” even before the year 2020. The failure of the  
2015-2023 administration to follow up with the Greater Calabar Master Plan resulted to haphazard physical  
development without control in Calabar Metropolis (Obongha, Ukam & Inah, 2024). A critical examination of  
the Calabar urban master plan as compared to the existing land use patterns of Calabar Metropolis has not been  
carried out and, therefore, becomes a gap which this study is meant to fill up.  
MATERIALS AND METHOD  
This research employed the survey design method. The survey design method took both qualitative and  
quantitative approaches. The qualitative approach involved the use of focus group professional interviews and  
questionnaire administration for qualitative data collection and description. The quantitative approach involved  
the use of scaled measurements which considered the following: (i) GIS-based mapping and (ii) bivariate  
analyses of variables on land uses. The bivariate analyses of land use were done, using a One-Way ANOVA  
analysis. The analysis was to determine whether there is a difference between the master plan and the existing  
land uses of Calabar Metropolis. Two methods were employed for data collection, namely: (i) Map analysis of  
the spatial area (m2) of land uses zoned in the Calabar urban master plan and the existing land uses and (ii)  
administration of a structured questionnaire.  
Map analysis: an existing land use map of Calabar Metropolis was obtained from the Cross River State  
Geographic Information Agency. From the map, major land uses were identified and compared with the Calabar  
urban master plan of 1973. Both the existing land use map and the Calabar urban master plan were critically  
studied and compared for the purpose of identifying similarities and differences in land uses. Map analysis was  
complimented with empirical verification of features on the landscape using Google Earth Imagery and  
reconnaissance survey to establish the functional relationship between the two maps using the linear planimeter  
(Roser, Leiborici, and Jackson, 2011).  
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The linear planimeter is a standard measuring tool/instrument in the field of Urban Planning, Cartography,  
Geography, Land Surveying, Architecture, and Engineering which is used in determining euclidean  
distances/spatial area, demarcating boundaries and parcels of land on a map ((Roser, et al., 2011). The usefulness  
of the linear planimeter to this study cannot be overemphasized. Its measurements were taken, using the map  
scale and represented in metres. Likewise, a questionnaire was also used in this study. The questionnaire was  
designed using responses on a Likert scale to measure land use patterns and compliance with the Calabar urban  
master plan. It contains questions with options such as Strongly Agreed (5 points), Agreed (4 points), Strongly  
Disagreed (1 point), Disagreed (2 points) and Undecided (3 points).  
The questionnaire was used to collect qualitative data which complimented data from measurements carried out  
using the linear planimeter. Data obtained from the administration of the questionnaire were not used in testing  
the hypothesis, rather were used for description of evidence-based information on incongruous land uses in  
Calabar Metropolis.  
The respondents were heads of household. The respondents were sampled from the total households of Calabar  
Metropolis with a sample size of 494 household heads. The population was 630,628 people. In this study,  
households were used as the sample frame. An average of six (6.0) people is officially accepted as household  
size in Nigeria (National Bureau of Statistics, 2021). Therefore, an average household size of six people from  
the total population of 630,628 people, making a total number of 105,105 households was used for the study.  
Data Analysis  
The Calabar Urban Master Plan and existing land use patterns  
Table 1.0 showed data on land use types, location and area of coverage (m2) as depicted in the Calabar urban  
master plan of 1973 and the existing land use patterns of Calabar Metropolis of 2023. The variables are the  
Calabar urban master plan (X1) and the existing land use patterns of Calabar Metropolis (X2).  
Table 1.0: Area (m2) of land uses depicted in the Calabar urban master plan and the existing land use  
patterns of Calabar Metropolis  
S/No  
Land use  
Type  
Location  
Calabar urban master Existing land  
plan area (m2) (X1)  
area (m2) (X2)  
1.  
Residential  
Akim Qua Town  
Big Qua Town  
Duke/Cobhom Town  
Ediba Qua Town  
Efut Abua  
50,300  
20,250  
21,800  
38,599  
29,600  
29,750  
41,890  
29,120  
32,550  
22,670  
58,990  
20,800  
22,900  
39,900  
30,750  
40,300  
41,900  
30,300  
54,600  
22,700  
Efut Anantigha  
Efut Ekondo  
Efut Uwanse  
Ekorinim 1 and 2  
Esin Ufot  
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Essien Town  
Henshaw Town  
Ikot Ansa  
27,900  
32,678  
41,800  
22,670  
40,480  
34,150  
32,700  
43,900  
45,700  
46,500  
55,900  
50,200  
42,500  
714,690  
Ikot Effanga Mkpa  
Ikot Ishie  
Ikot Omin  
Mbukpa  
49,300  
29,580  
560,937  
Nyahasang  
Total  
2.  
Commercial  
Watt Market  
1,256  
867  
96  
1,600  
1,050  
107  
110  
189  
87  
Marian Market  
Ishie Market  
Akim Market  
101  
122  
Mbukpa Market  
Ikot Omin Market  
Ikot Ansa Market  
Bacoco Market  
Atakpa Market  
Uwanse Market  
Goldie Market  
Abasi Obori Market  
Beach Market  
98  
112  
76  
65  
54  
88  
120  
113  
117  
77  
Anantigha Market  
Edim Otop Market  
Nyahasang Market  
Total  
2,442  
3,800  
4,063  
3.  
Industrial  
Northern Estate  
501  
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Southern Estate  
Jonathan by-pass  
Total  
3,500  
7,300  
411  
517  
1,429  
4.  
Institutional  
Federal/State  
Secretariats  
4,784  
6,590  
4,550  
4,300  
1,021  
1,450  
2,650  
3,982  
28,790  
3,500  
900  
1,104  
6,100  
4,400  
4,200  
1,000  
1,400  
2,600  
3,082  
22,260  
3,350  
600  
Army lands  
Navy lands  
Police lands  
Fire Service lands  
Prison lands  
Immigration/Customs  
lands  
Hospitals land  
Higher education land  
Airport land  
1,850  
64,367  
877  
Cultural Centre  
Water Board land  
Total  
50,973  
5.  
Cemeteries  
Ikot Ansa  
Goldie  
1,200  
1,090  
1,659  
1,200  
1,090  
1,650  
950  
Hawkins  
Etta Agbor Layout  
Essien Town  
Total  
800  
3,949  
5,690  
6.  
Open Space  
Stadium  
Ishie  
800  
20  
900  
15  
Akim  
14  
10  
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Federal Housing Est.  
State Housing Estate  
Millennium Park  
Big Qua  
128  
114  
150  
11  
103  
77  
150  
10  
Mbukpa  
13  
10  
New airport  
Ikot Ansa  
3000  
12  
3,000  
09  
Gulf Club  
15  
10  
Henshaw Town  
Total  
08  
4,302  
4,307  
7.  
Wetlands  
Anantigha  
Akai Effa  
Idundun  
Bacoco  
37,670  
28,550  
23,750  
22,800  
112,770  
756,067  
12,627  
11,301  
12,408  
12,330  
48,666  
829,818  
Total  
Total  
= Neighbourhood zones and land uses not contained in the 1973 Calabar Urban Master Plan  
Source: Researcher’s Field Survey, 2025.  
With the data set in Table 1.0, the hypothesis formulated was however, tested. The Table 1.0 showed missing  
data in some neighbourhood zones that were not contained in the master plan as well as some land uses that were  
not in the master plan. Therefore, for the purpose of valid results, normality test was conducted on the data in  
Table 1.0 and made use of five data sets in each land use zone such as residential, commercial, industrial,  
institutional etc. for both existing land use patterns and the Calabar urban master plan for testing hypothesis one  
with the One-way ANOVA. The One-way ANOVA, for example, is used to estimate how the mean of  
a variable changes according to the level of an independent variable. One-way ANOVA was used because this  
study wants to know how an independent variable, in combination, affects a dependent variable. In the  
hypothesis stated above, the land uses zoned in the 1973 Calabar urban master plan and the existing land uses of  
Calabar Metropolis in 2023 were compared. ANOVA is mathematically expressed as:  
2
2
F = S1 /S2  
………………….………………………………………..……... eqn. 1  
The assumptions/conditions of the One-way ANOVA showed that:  
The dependent and independent variables should be continuous.  
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The populations (independent variable) from which the samples were obtained must  
or approximately distributed.  
be normally  
The variances of the population must be equal and  
The groups must have the same sample size.  
If these assumptions are not satisfied, the result that is gotten from the One-way ANOVA may not be valid.  
The hypothesis was tested using the One-way analysis of variance (ANOVA). The Calabar urban master plan  
(X1) as the independent variable and the existing land use patterns (X2) as the dependent variable. The Test result  
is presented on Table 2.0. The Table 2.0 showed that the existing land use patterns of Calabar Metropolis in  
2023 and the land uses depicted in the 1973 Calabar urban master plan are statistically different. F values were  
highly positive at 0.001 level of significance. This is because 0.001 is ≤ 0.05 confidence level at 95.0 per cent  
confidence interval. Therefore, it has been established that the result showed a statistically significant difference  
between the existing land use patterns of Calabar Metropolis and the Calabar urban master plan (Table 2.0).  
Table 2.0: One-way ANOVA between the Calabar urban master plan and the existing land use patterns  
Source: Researcher’s data analysis, 2025.  
The levene’s test of equality of error variances or the homogeneity of variance was used to test the assumption  
that variances were equal across groups or samples. From the Table 3.0 P-value of 0.001 ≤ 0.05 confidence level  
(based on the mean and median which implied that the assumption of equal variance across groups) was  
significant. The homogeneity assumption of variance was not met which implied the variances were significantly  
different from each other. Nevertheless, this assumption did not impede the progress to analysis of variance,  
using the P-value of 0.001 (Table 3.0).  
Table 3.0:  
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The result was also illustrastrated with the ANOVA plot (Figure 2.0). The ANOVA plot showed the estimated  
marginal means that represent the difference between the existing land use patterns of 2023 and the Calabar  
urban master plan of 1973. The slope of the plot pointing upward explains the land area (m2) in which the existing  
land use patterns have not complied with the prescriptions of the Calabar urban master plan. This difference has  
also been demonstrated in Figures 3.0 and 4.0.  
Table 4.0:  
Table 5.0:  
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Table 6.0:  
Scheffe post hoc test of multiple comparison in the above table shows there is significant difference between  
residential and commercial, institutional, cemeteries, open space and wetland in the first row (p < 0.01)  
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Figure 2.0: ANOVA Plot showing estimated marginal difference between the master plan and the existing land  
use patterns of Calabar Metropolis  
Source: Researcher’s data analysis, 2025.  
The analysis in Figure 3.0 was derived from Table 1.0. It is a graphical representation of the land use zones  
depicted in the Calabar urban master plan and the existing land uses. Figure 5.0 showed the land area used up  
by the existing land use patterns of Calabar Metropolis and the direction of extension towards the wetlands.  
800000  
700000  
600000  
500000  
400000  
300000  
200000  
100000  
0
Land use zones  
Calabar urban master plan area  
Existing land area  
Figure 3.0: Bar graph derived from Table 1.0 showing the land area of the master plan and the existing land  
use zones.  
Source: Researcher’s compilation, 2025.  
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Responses on compliance with the Master Plan/existing land use patterns  
Table 7.0 showed responses on the Likert scale in compliance/non-compliance with the Calabar urban master  
plan. The Table 4.0 showed responses on land use development with a corresponding five (5) options on the  
Likert scale which explained the degree of acceptability of the observed urban land use development in  
compliance with the Calabar urban master plan. The five (5) options on the Likert scale include the following:  
strongly agree (5 points); that is if the respondents strongly agreed with applicability of the observed land use  
development as not in total compliance with the master plan. Agree (4 points); that is if the respondents merely  
agreed with the applicability of the observed land use development as not in compliance with the master plan.  
Strongly disagree (1 point); that is if the respondents were not totally in agreement with the observed land use  
development as not in compliance with the master plan. Disagree (2 points); if the respondents were not in  
agreement with the observed land use development due to non-compliance with the master plan and undecided  
(3 points); if respondents were those without any meaningful judgement on the observed land use development  
or had no idea with the master plan.  
The Likert scale measured whether flood plains in Calabar Metropolis have been developed for residential  
housing and other land uses. About 152 respondents strongly agreed, 136 respondents agreed, 89 respondents  
strongly disagreed, 106 respondents disagreed, and 11 respondents were undecided making a total of 494  
responses. Respondents who strongly agreed to all questions on the Likert scale make up (25.30 per cent), those  
that agreed (24.53 per cent), strongly disagreed (17.54 per cent), disagreed and undecided were (20.70 per cent)  
and (11.90 per cent) respectively. However, the average percentage mean response on the Likert scale is 32.12  
per cent.  
The Likert scale is mathematically expressed as:  
R11 = ⅀W∕AN (0≤ R11≥1) …………………………………………………… eqn. 2  
Where: R11 = Relative importance index  
⅀ = summation  
W = weight given to each factor by the respondents (1-5)  
A = highest weight (in this study 5)  
N = sample size (in this study 494)  
However, R11 falls within the range of zero to one (0-1) making it possible to compare opinions. Therefore, the  
benchmark for deciding the significant score is 0.05 as such values ≥ 0.05 are considered not significant while  
values ≤ 0.05 are significant. Responses on the Likert scale are considered as qualitative in this study and were  
not tested further.  
Table 7.0: Responses on the Likert Scale concerning compliance/non-compliance with the Calabar urban  
master plan  
Responses on land use  
development  
Scoring Method  
Strongly  
Agree  
Agree  
Strongly  
Disagree  
Disagree Undec Total  
ided  
Mean  
Flood plains are being 152  
136  
89  
106  
11  
494  
327.6  
developed  
residential/other uses  
for  
(760)  
(544)  
(89)  
(212)  
(33)  
(1638)  
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Wetlands sand-filled for 42  
settlements  
45  
157  
(157)  
24  
152  
(304)  
32  
98  
494  
229  
(210)  
(180)  
168  
(294)  
96  
(1145)  
494  
Locations of some open 174  
375.2  
markets  
conforming  
are  
such  
not  
as  
(870)  
(656)  
(24)  
(64)  
(288)  
(1878)  
Atakpa, 8 Miles and Abasi  
Obori/Goldie  
Some cemeteries not in 158  
compliance with the master  
plan  
137  
96  
88  
15  
494  
338.2  
245.8  
(790)  
(548)  
(96)  
(176)  
(45)  
(1691)  
Many public institutions 44  
are adjacent injurious land  
53  
106  
182  
109  
494  
(220)  
(212)  
(106)  
(364)  
(327)  
(1229)  
uses such as University of  
Calabar/Airport  
Residential  
interspersed  
industries  
areas 175  
with  
141  
59  
64  
55  
494  
358.2  
367.6  
(875)  
(564)  
(59)  
(128)  
(165)  
(1791)  
Recreational land uses are 151  
183  
36  
57  
67  
494  
inadequate  
interspersed  
and  
with  
(755)  
(732)  
(36)  
(114)  
(201)  
(1838)  
educational uses such as  
stadium and state library  
Reserved open spaces are 217  
built-up by the affluent  
example, State housing  
193  
49  
33  
2
494  
395.6  
289  
(1085)  
(772)  
(49)  
(66)  
(6)  
(1978)  
Non-conforming land uses 95  
are frequent in Calabar  
126  
105  
143  
25  
494  
(475)  
(504)  
(105)  
(286)  
(75)  
(1445)  
Metropolis  
Public land uses are often 99  
96  
111  
89  
99  
494  
293  
encroached  
residential/industrial  
by  
(297)  
(495)  
(384)  
(111)  
(178)  
(1465)  
example, UNICROSS and  
Water Board  
Many cultural areas have 69  
been destroyed such as  
Cultural centre complex  
57  
121  
178  
69  
494  
251.4  
(345)  
(228)  
(121)  
(356)  
(207)  
(1257)  
Total  
1,376  
25.30  
1,335  
24.53  
953  
1,124  
20.70  
646  
5,434  
100  
3212.4  
32.12  
Percentage  
17.54  
11.90  
Source: Researcher’s compilation from Field Survey, 2025.  
Page 300  
250  
200  
150  
100  
50  
0
Strongly Agree  
Agree  
Strongly Disagree  
Land uses  
Disagree  
Undecided  
Figure 5.0: Bar graph derived from Table 7.0 showing responses on compliance with the Calabar urban master  
plan in the Likert Scale  
Source: Researcher’s compilation, 2025.  
The Table 7.0 was used to generate Figure 5.0, a bar graph which showed that 1,376 (25.30 per cent) represents  
responses on strongly agreed to all the observed land use developments not in compliance with the master plan.  
1,335 (24.53 per cent) responses agreed to all the observed land use developments not in compliance with the  
master plan. 953 (17.54 per cent) responses strongly disagreed and 1,124 (20.70 per cent) responses disagreed  
to all the observed land use developments not in compliance with the master plan. 646 (11.90 per cent) responses  
were undecided. The questions were all tailored towards illegality and non-compliance with the Calabar urban  
master plan. All land use developments are represented in different bars (Figure 5.0).  
DISCUSSION  
The null hypothesis, which sought to know whether there is a significant difference between the land area zoned  
for residential use, commercial use, industrial use, institutional use, open spaces, cemeteries and wetlands in the  
Calabar urban master plan and the currently existing land area (Table 1.0). The result, therefore, accepted the  
alternative hypothesis (Hi) which states that there is a significant difference between the existing land use  
patterns of Calabar Metropolis and the Calabar urban master plan. This means that land allocated to some uses  
in the Calabar urban master plan were found to be different from the currently built-up land uses (physical  
development) of Calabar Metropolis. The One-way ANOVA (Tables 2.0 and 3.0) was the test statistic used in  
this analysis. It showed a statistically significant relationship and goodness of fit in the data sets, with p-value of  
0.001 level of significance ≤ 0.05 level of confidence. This result was also proven by producing different  
statistical plots, such as the estimated marginal difference plot (Figure 2.0), bar graph (Figure 3.0) and existing  
spatial patterns of Calabar Metropolis in a map (Figure 4.0). They were meant to show the difference between  
land area of the master plan and the land area of the existing land use patterns of Calabar Metropolis.  
The Likert scale (Table 7.0) was also used qualitatively to compliment the result from the test statistic. Responses  
on the Likert scale measured whether there is compliance with the master plan from current land use development  
in Calabar Metropolis. These responses indicated that the master plan has been altered (Figure 5.0). The  
professionals were also interviewed separately and their responses confirmed a significant variation in the level  
of current physical developments from the prescription of the master plan.  
The implication of this result is that there is no controlled development in Calabar Metropolis. The prescription  
of the master plan has not been followed strictly, and there are no strong institutions to monitor/control  
Page 301  
development. The Town Planning Department has been sidelined over the years from controlled development  
and in urban land use administration. For example, many land uses contravened the master plan. These land uses  
include the following: cemeteries at Etta Agbor layout, and Spring Road; conversion of open spaces in the State  
Housing Estate to residential plots; building of gasoline stations in a high-class residential zone (such as the  
Federal Housing Estate); and conversion of wetland zones meant for urban agriculture to residential and other  
developments.  
In order to determine the degree of conformity of existing land use patterns of Calabar Metropolis with the  
Calabar urban master plan empirical verifications were also sought. The results pointed to the fact that current  
developments in Calabar Metropolis violated the prescriptions of the master plan. However, Nallathiga (2016)  
pointed out that the role of the master plan is to control both physical and economic developments; direct land  
uses and improves the quality of lives of the residents. This study, therefore, showed a deviation from these roles  
performed by the master plan as a result of unguarded developments. The observation of Hersperger, et al.,  
(2015) that land uses contravening the master plan have resulted to conflicts and development of nuisances,  
criminalities, and aesthetic disappearance. These incidents were seen in the result of this study where land uses  
developed in contravention with the master plan have produced several nuisances that are aesthetically  
unpleasant to the residents of Calabar Metropolis.  
A study by Tudor, et al., (2013) found that cemeteries are non-conforming with residential zones. In the Calabar  
urban master plan, three cemeteries were zoned at Ikot Ansa (north), Goldie (central), and Hawkins (south) but  
this study also found two cemeteries existing at Etta Agbor layout and Spring Road, Essien Town zone.  
Therefore, these two cemeteries found are regarded as non-conforming land uses. The result, therefore, a  
confirmation of the segregation component of the ecological theory which emphasized the need for separation  
of antagonistic land uses and the association of conforming land uses (Park, 1950).  
CONCLUSION  
There is need to strengthen institutions responsible for land use administration and development control.  
This would help to reduce the rate of contravention with the Calabar urban master plan.  
There is need for urgent review of the 1973 Calabar urban master plan.  
The Planning Authority should be empowered to monitor development and redevelopment in order to  
ensure that land uses are developed and distributed according to the design in the master plan.  
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